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Influence of instantaneous and time‐averaged groundwater flows induced by waves on the fate of contaminants in a beach aquifer
Author(s) -
Malott Spencer,
O'Carroll Denis M.,
Robinson Clare E.
Publication year - 2017
Publication title -
water resources research
Language(s) - English
Resource type - Journals
SCImago Journal Rank - 1.863
H-Index - 217
eISSN - 1944-7973
pISSN - 0043-1397
DOI - 10.1002/2017wr020948
Subject(s) - aquifer , residence time (fluid dynamics) , groundwater , soil science , hydrology (agriculture) , environmental science , sediment , geology , flow (mathematics) , surface water , mechanics , geotechnical engineering , geomorphology , environmental engineering , physics
Abstract Wave‐induced water exchange and groundwater flows in beach aquifers impact the fate of contaminants including nutrients, fecal bacteria, and nonaqueous phase liquids (NAPLs). Waves induce high‐frequency fluxes in shallow beach sediments. In addition, the phase‐averaged effect of waves (wave setup) drives deeper flow recirculations through a beach aquifer. Field data of shallow instantaneous and time‐averaged vertical head gradients (fluxes) are first compared with deeper time‐averaged fluxes over a period of varying wave conditions. The time‐averaged fluxes are equivalent to that which would be simulated assuming a phase‐averaged water surface (i.e., wave setup). Based on this comparison, the need to simulate phase‐resolved wave motion versus the simplified phase‐averaged water surface in predicting contaminant fate is evaluated. While high‐frequency fluxes cause large surface water volumes to filter through beach sediments, the exchanging water has a short residence time (<1–70 s). The time‐averaged flow behavior captures exchanging water with longer residence time (hours to months) and deeper flow paths. Therefore, consideration of the time‐averaged behavior may be sufficient for evaluating dissolved reactive constituents. In contrast, calculations indicate that instantaneous fluxes may need to be considered in evaluating colloidal contaminants (e.g., particulate organic matter and fecal bacteria) as sediment interactions affect their transport and residence time. Finally, multiphase simulations illustrate the differential effect of considering instantaneous versus time‐averaged fluxes on the downward migration of NAPL in beach sediments. This study provides an important foundation for future field and modeling efforts focused on understanding and predicting contaminant transport in wave‐influenced beaches.